Field sampling in October 2024 at 9β10 stations (the abstract says 10, methods say 9 β an internal inconsistency) recorded 1,248 macrozoobenthos individuals across Bivalvia, Gastropoda, and Malacostraca; the most abundant species was Cerithideopsilla alata (270 individuals). Shannon diversity ranged 1.09β2.38, evenness 0.56β0.89, dominance 0.11β0.49, and density 17β104 ind/mΒ². Surface SOC (0β20 cm) averaged 62.19 Mg/ha, lowest at station 3 (23.95 Mg/ha, low NDVI cover) and highest at station 9 (96.56 Mg/ha, high cover) .
The key finding is that SOC correlates "very weakly" with community structure: r β 0.01 (diversity), 0.03 (evenness), 0.33 (dominance, negative β0.05 in conclusion β another internal inconsistency), per PCA and Excel-based correlation. Critically, no significance tests, p-values, confidence intervals, or sample sizes for the correlation are reported, and the values themselves are ambiguously labeled . With n β 9 stations, an r of 0.01β0.03 is statistically indistinguishable from zero; the honest conclusion is that SOC does not predict macrozoobenthos structure at this site, not that it "contributes weakly."
The measured SOC range (23.95β96.56 Mg/ha, 0β20 cm) sits far below regional benchmarks β mangrove SOC stocks in Guinea-Bissau reached 132.33 Β± 9.01 Mg/ha and Venezuelan Rhizophora soils ~10β20 wt% TOC . Also note the exact species name "Saccostrae cuccullata" is likely a misspelling of Saccostrea cucullata, and NDVI-based station categorization is asserted but the NDVI values are not shown.
Descriptively useful as a local baseline (species list, SOC gradient linked to vegetation cover), but the correlation analysis is underpowered, unlabeled, and untested; conclusions should be treated as provisional. The "balanced community / no dominance" claim conflicts with the reported dominance index range of 0.11β0.49 at the station level.
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